|Scientific Name:||Syngnathus abaster Risso, 1827|
Syngnathus abaster ssp. ganzirrensis D'Ancona, 1934
Syngnathus agassizii Michahelles, 1829
Syngnathus algeriensis Günther, 1870
Syngnathus anguisigola Nardo, 1847
Syngnathus bucculentus Rathke, 1837
Syngnathus caspius Eichwald, 1831
Syngnathus ethon Risso, 1827
Syngnathus ethon ssp. aeolicus Di Caporiacco, 1948
Syngnathus flavescens Kaup, 1856
Syngnathus microchirus Moreau, 1891
Syngnathus nigrolineatus Eichwald, 1831
Syngnathus nigrolineatus ssp. maeoticus Slastenenko, 1938
|Taxonomic Source(s):||Risso, A. 1827. Histoire naturelle des pricipales productions de l'Europe méridionale. 5(i-vii): 1-403.|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Reviewer(s):||Ralph, G. & Freyhof, J.|
|Contributor(s):||Kottelat, M. & Freyhof, J.|
Syngnathus abaster is a freshwater and estuarine pipefish species that inhabits coastal waters and lower reaches of rivers throughout the Caspian, Black, and Mediterranean Seas, the Atlantic coast of Europe to the Bay of Biscay, and several rivers in northern Europe and Russia. The species occupies a wide variety of habitats, and there are no known threats. Therefore S. abaster is listed as Least Concern.
|Previously published Red List assessments:|
|Range Description:||Syngnathus abaster inhabits coastal waters and lower reaches of rivers in the Caspian, Black and Mediterranean Sea basins, the Atlantic coast from Gibraltar to the southern Bay of Biscay; in the Danube reaching the Romanian-Hungarian border, and in the Dniepr reaching Kiev. The species has been introduced in reservoirs of the middle and lower Volga with mysids brought from the Don estuary, now spreading and already south of Moscow.|
Native:Albania; Algeria; Azerbaijan; Bosnia and Herzegovina; Bulgaria; Croatia; Cyprus; Egypt; France; Georgia; Gibraltar; Greece; Iran, Islamic Republic of; Israel; Italy; Kazakhstan; Lebanon; Libya; Moldova; Monaco; Montenegro; Morocco; Palestinian Territory, Occupied; Portugal; Romania; Russian Federation; Serbia; Slovenia; Spain; Syrian Arab Republic; Tunisia; Turkey; Turkmenistan; Ukraine
|FAO Marine Fishing Areas:|
Atlantic – northeast; Mediterranean and Black Sea
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||To date there have been no dedicated range-wide surveys or population estimates for S. abaster, but it is known to be common and abundant. Further research is needed in order to determine population size and trends in abundance for this species.|
|Current Population Trend:||Unknown|
|Habitat and Ecology:||Syngnathus abaster inhabits a wide range of marine, brackish- and fresh-water habitats, and is mostly associated with dense submerged vegetation but is also found on open mud bottom substrates (Kuiter 2000).|
They live up to four years and spawn for the first time at one year. The spawning season occurs from April-October (Silva et al. 2006a). This species is ovoviviparous, and females lay eggs into a brood pouch on the ventral surface of the tail of males. Males fertilize the eggs as they enter the pouch. Eggs incubate in the male's brood pouch for about 20-25 days, followed by live birth (Silva et al. 2006b). This species is polygynandrous (Hubner et al. 2013). They likely feed on small invertebrates such as crustaceans, similar to other pipefish species (e.g., Garcia et al. 2005, Kendrick and Hyndes 2005). They reach a maximum length of 21 cm (Kuiter 2000).
|Use and Trade:||Although this species has not been directly identified in trade, pipefishes in general are often targeted and/or caught as bycatch and then traded for use in traditional medicine, as curios, and for the aquarium trade (Vincent et al. 2011). This species may be involved but it has not been recorded.|
|Major Threat(s):||There are no major threats known to be impacting this species.|
|Conservation Actions:||There are no species-specific conservation measures in place for S. abaster. The species occurs in several protected areas throughout its range. It is not mentioned in any international legislation or trade regulations.|
Garcia, A M., Geraldi, R.M. and Vieira, J.P. 2005. Diet composition and feeding strategy of the southern pipefish Syngnathus folletti in a Widgeon grass bed of the Patos Lagoon Estuary, RS, Brazil. Neotropical Ichthyology 3(3): 427-432.
Hubner, K., Gonzalez--Wanguemert, M., Diekmann, O. E., and Serrao, E. A. 2013. Genetic evidence for polygynandry in the black-striped pipefish Syngnathus abaster: A microsatellite-based approach. Journal of Heredity 104(6): 791-797.
IUCN. 2016. The IUCN Red List of Threatened Species. Version 2016-3. Available at: www.iucnredlist.org. (Accessed: 07 December 2016).
Kendrick, A.J. and Hyndes, G.A. 2005. Variations in the dietary compositions of morphologically diverse syngnathid fishes. Environmental Biology of Fishes 72: 415-427.
Kottelat, M. and Freyhof, J. 2007. Handbook of European Freshwater Fishes. Publications Kottelat, Cornol, Switzerland.
Kuiter, R.H. 2000. Seahorses, Pipefishes and Their Relatives: A Comprehensive Guide to Syngnathiformes. TMC Publishing, Chorleywood, England.
Silva, K., Monteiro, M.N., Vieira, M.N. and Almada V.C. 2006. Reproductive behaviour of the black striped pipefish Sygnathus abaster (Pisces, Sygnathidae). Journal of Fish Biology 69: 1860-1869.
Silva, K., Monteiro, N.M., Almanda, V.C. and Vieira, M.N. 2006. Early life history of Sygnathus abaster. Journal of Fish Biology 68: 80-86.
Svetovidov, A.N. 1964. [Fishes of the Black Sea]. Nauka, Moskva.
Vincent, A.C.J., Foster, S.J. and Koldewey, H.J. 2011. Conservation and management of seahorses and other Syngnathidae. Journal of Fish Biology 78: 1681-1724.
|Citation:||Pollom, R. 2016. Syngnathus abaster. The IUCN Red List of Threatened Species 2016: e.T21257A19423178.Downloaded on 18 March 2018.|
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